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    • 专利摘要:
    Process for producing bio methane by biogas purification from non-hazardous waste storage facilities (ISDND) according to which: - the initial gas flow is compressed, - the stream of gas to be purified is introduced into at least one modulated adsorber in pressure (PSA) loaded with adsorbents capable of reversibly adsorbing VOCs, the gaseous stream is subjected to at least one membrane separation to partially separate the CO2 and O2 from the gas stream, and the retentate resulting from the membrane separation is introduced. in at least one temperature-modulated adsorber (PTSA) loaded with adsorbents capable of reversibly adsorbing most of the remaining CO2, the gas stream is subjected to cryogenic separation in a distillation column to separate the O 2 and N 2 from the gaseous flow, - the CH4-rich stream from the cryogenic separation is recovered. Installation for the implementation of the process
    公开号:FR3046086A1
    申请号:FR1563357
    申请日:2015-12-24
    公开日:2017-06-30
    发明作者:Guenael Prince；Mathieu Lefebvre；Pierre Briend；Nicolas Paget
    申请人:Waga Energy；
    IPC主号:
    专利说明:

    PROCESS FOR THE PRODUCTION OF BIOMETHANE BY PURIFYING BIOGAS FROM NON-HAZARDOUS WASTE STORAGE FACILITIES QSDNDI AND INSTALLATION FOR IMPLEMENTING THE PROCESS The subject of the invention is a process for the production of bio-methane by purification of biogas derived from non-hazardous waste storage facilities (ISDND). It also relates to an installation for implementing the method.
    More specifically, the present invention relates to a method of treatment by coupling a membrane permeation and a cryogenic distillation of a gaseous stream containing at least methane, carbon dioxide, air gases (nitrogen and oxygen) and pollutants (LLS and volatile organic compounds (VOCs)). The objective is to produce a gaseous stream rich in methane whose methane content is in line with the needs of its use and to limit as much as possible the impact of CH4 discharges into the atmosphere (gas with a high greenhouse effect) . The invention relates in particular to the purification of biogas from non-hazardous waste storage facilities, hereinafter ISDND (Non-Hazardous Waste Storage Facility), with the aim of producing biomethane in accordance with the injection into a natural gas system or in local use as a vehicle fuel.
    The anaerobic digestion of organic wastes in ISDNDs produces a significant amount of biogas throughout ISDND's lifetime and even several years after shutdown and closure of ISDND. By its main constituents - methane and carbon dioxide - biogas is a powerful greenhouse gas; At the same time, it constitutes a significant source of renewable energy in the context of the scarcity of fossil fuels.
    Biogas contains several polluting compounds and must be purified to allow commercial development. There are several processes for recovering and purifying biogas.
    Biogas mainly contains methane (CH4) and carbon dioxide (CO2) in varying proportions depending on the method of production. In the case of ISDND biogas, the gas also contains a proportion of air gases (nitrogen and oxygen) and, to a lesser extent, water, hydrogen sulphide, and volatile organic compounds. (VOC).
    According to the degraded organic matter, the techniques used and the particular conditions (climates, typologies ..) of each ISDND, the proportions of the biogas components differ. Nevertheless, on average, the biogas comprises, on dry gas, 30 to 60% of methane, 15 to 50% of CO2, 0 to 30% of nitrogen, 0 to 6% of oxygen, 0 to 1% H2S and a few tens to a few thousand milligrams per normal cubic meters of VOCs and a number of other trace impurities.
    Biogas is valued in different ways. It may, after partial treatment, be recovered near the production site to provide heat, electricity or both (cogeneration). The high content of carbon dioxide reduces its calorific value, increases the compression and transport costs and limits the economic interest of its valuation to this use of proximity.
    Further purification of the biogas allows its wider use. In particular, a thorough purification of the biogas makes it possible to obtain a biogas purified to the specifications of natural gas and which can be substituted for it. The biogas thus purified is called "biomethane". Biomethane thus completes the natural gas resources with a renewable part produced in the heart of the territories. It is usable for exactly the same uses as natural gas of fossil origin. It can feed a natural gas network, a filling station for vehicles. It can also be liquefied to be stored and transported as liquefied natural gas (LNG).
    The modes of valorization of the biomethane are determined according to the local contexts: local energy needs, possibilities of valorization as biomethane fuel, existence close to networks of distribution or transport of natural gas in particular. Creating synergies between the different actors working on a territory (farmers, industrialists, public authorities), the production of biomethane helps the territories to acquire a greater energy autonomy.
    It should be noted that, depending on the country, environmental regulations often impose constraints on atmospheric discharges. It is indeed necessary to put in place technologies that limit the impacts of greenhouse gases (CH4) and pollutants (H2S and VOCs) contained in biogas. It is therefore important to have a high CH4 yield (equal, by mass, to the amount of CH4 recovered relative to the amount of CH4 contained in the biogas) and to provide treatment systems for rH2S and VOCs that avoid releases. atmospheric.
    Moreover, an additional problem remains the presence of O 2, which, during the separation of the mixture, can generate an explosive atmosphere during the various enrichment stages. This risk of creating an explosive mixture makes the landfill biogas particularly difficult to purify safely and economically.
    The document US Pat. No. 8,221,524 B2 describes a process for enriching a gas with CH4, up to 88% by different recycling steps. The process consists of compressing the gas stream and then passing it over an adsorbent to remove VOCs. The gas stream is then subjected to a membrane separation step and then to a pressure swing adsorption step (PSA). The adsorbent used in the PSA is of the CMS (carbon molecular sieve) type and makes it possible to eliminate the N 2 and a small part of the O 2.
    EP1979446 discloses a biogas purification process of removing H2S, compressing the gas, filtering it to remove particles. The gas is then subjected to a membrane separation step to remove CO 2 and O 2, drying by passing through a PSA then in different filters and finally again in a PSA to remove the N2. The gas is finally liquefied.
    US2004 / 0103782 discloses a biogas purification process of removing H2S, compressing the gas, filtering it to remove particles, subjecting it to a pressure swing adsorption (PSA) step to remove VOC, then to membrane separation to remove most of the CO 2 as well as a fraction of the O 2.
    Document US Pat. No. 5,486,227 describes a process for purifying and liquefying a gaseous mixture consisting of subjecting the stream to a temperature-modulated adsorption (TSA) to eliminate FFI2S in particular, and then to a pressure-swing adsorption (PSA) to remove CO2. in particular, then finally to a cryogenic separation to eliminate the nitrogen and to retain only the methane.
    US5964923 and US5669958 disclose a method of treating a gaseous effluent comprising dehydrating the gas, condensing it through an exchanger, subjecting the gas to membrane separation, and then cryogenic separation.
    US2010 / 077796 discloses a purification process of subjecting the gaseous stream to a membrane separation, treating the permeate in a distillation column, and then mixing the methane gas from the column, after vaporization, with the retentate obtained at room temperature. the outcome of membrane separation.
    Documents US3989478 and FR2917489 describe cryogenic systems for purifying a methane-rich stream. Both systems use a PSA to knock down the CO2 before the liquefaction stage. In US3989478, the regeneration of the PSA is carried out through the nitrogen-rich distillate recovered at the top of the distillation column. In the document FR2917489, the regeneration of the PSA is carried out by the liquid methane withdrawn at the bottom of the distillation column.
    EP0772665 discloses the use of a cryogenic distillation column for the separation of mine gas composed mainly of CH4, CO2 and N2.
    None of the cited documents addresses the problem of providing safe biomethane related to ΙΌ2, a methane concentration greater than 95%, a CO2 concentration of less than 2.5% and a methane yield greater than 85%.
    The problem that the invention proposes to solve is that of providing a biogas purification process that complies with the above constraints, that is to say a process that is safe, with optimum yield, producing a biomethane of high quality substitutable for natural gas and which respects environmental standards, particularly with regard to the destruction of polluting compounds such as VOCs and compounds with a high greenhouse effect such as CH4. The gas thus produced may be recovered in liquid or gaseous form either by injection into a gas network or else for mobility applications.
    To solve this problem, the Applicant has coupled 4 technologies respectively a VOC purification through PSA, a first purification of CO2 through a membrane separation, a second purification of CO2 through PTSA and finally a purification ΓΝ2 and ΓΟ2 through cryogenic separation.
    More specifically, the subject of the invention is a process for producing bio methane by biogas purification from non-hazardous waste storage facilities (ISDND) according to which: the initial gas stream is compressed, the stream is introduced; of gas to be purified in at least one adsorber modulated in pressure (PSA) loaded with adsorbents capable of reversibly adsorbing the VOCs, - the depleted VOC gas stream leaving the PSA is subjected to at least one membrane separation to partially separate the CO2 and ΓΟ2 of the gaseous stream, the retentate originating from the membrane separation is introduced into at least one temperature-modulated adsorber (PTSA) loaded with adsorbents able to reversibly adsorb most of the remaining CO2, the gaseous stream depleted in CO2 is subjected to, leaving from PTSA to a cryogenic separation in a distillation column to separate ΓΟ2 and ΓΝ2 from the gas stream, - the rich CH4 stream from the cryog separation is recovered ene.
    In a preferred embodiment, the PSA is regenerated by means of the permeate resulting from a first membrane separation. Similarly, PTSA is regenerated by means of the CH4-rich stream or N2-rich distillate from the cryogenic separation. The permeate obtained from a second membrane separation is oxidized after mixing with the nitrogen-rich distillate from the cryogenic separation.
    Advantageously, before compression, the gas to be purified is dried and then subjected to a desulfurization step. The drying step consists in supercharging the gas, from 20 to a few hundred millibars (maximum 500 mbar maximum), also making it possible to avoid air inlets in the pipes. The overpressure allows preliminary drying by cooling the biogas between 0.1 and 10 ° C, to condense the water vapor. The outgoing gas flow therefore has a pressure of between 20 and 500 mbar and a dew point of between 0.1 ° C. and 10 ° C. at the outlet pressure. The desulfurization step ensures the capture of FILS in order to meet the quality requirements of the network and to avoid the rapid degradation of the materials in the following process. In addition, it is important to have a capture step that fixes H2S in a stable form (such as solid sulfur) to avoid any harmful emissions to health and the environment (odor nuisance, formation of SOx) . This treatment is preferably carried out with active carbons or iron hydroxides in tanks with volumes adapted to the amount of H 2 S to be treated. The H2S is thus transformed into solid sulfur. The outgoing gas stream in practice contains less than 5 mg / Nm3 of H2S.
    According to the method, the gas stream to be treated is then compressed. The compression is carried out at a pressure of between 8 and 24 bars. This pressure is necessary to enable the operation of the following steps and to reduce the size of the equipment. The compression is advantageously carried out with a lubricated screw compressor. The implementation of this type of compressor gives the possibility of possibly recovering the heat on the cooling circuit of the oil. In a preferred embodiment and as will be seen later, the heat is recovered to heat the gas that will be used to regenerate the PTSA. The next step is to purify the VOC gas stream. To do this, the stream of gas to be purified is passed through at least one adsorber modulated in pressure (PSA) loaded with adsorbents capable of reversibly adsorbing the VOCs. This step makes it possible to purify the biogas of VOCs (light hydrocarbons, mercaptans, siloxanes, etc.) that are incompatible with the quality requirements of the network and that may pollute the subsequent purification steps (especially the membranes).
    Advantageously, 2 PSAs are used so as to be able to implement the process continuously. Indeed, when the first PSA is saturated with VOC, it is substituted by the second PSA which itself has been previously regenerated.
    Preferably, the PSA (s) are regenerated by the permeate resulting from the membrane separation. This permeate is composed mainly of CO2 and a very low content of CH4 · In practice, the gas flow at the regeneration outlet is oxidized. In an advantageous embodiment, it is premixed with the N2-rich distillate from the cryogenic separation, the mixture then being oxidized. Alternatively, the PSA regeneration output gas stream and the N2-rich distillate from the cryogenic separation are oxidized separately.
    In the next step of the process of the invention, the CO2 is purified from the gas stream. To do this, the depleted VOC gas stream leaving the PSA is subjected to at least one membrane separation to partially separate the CO2 and ΓΟ 2 from the gas stream. More precisely, the selective separation of the membranes makes it possible to perform an efficient first purification of the biogas by separating a large part of the CO2 (more than 90%) as well as a part of ΓΟ2 (approximately 50%). Membrane scrubbing can be composed of 1, 2, 3 or 4 stages of membranes depending on the characteristics of the biogas. This step makes it possible to produce a gas with less than 3% CO2 and with a CH4 yield greater than 90%.
    In a particular embodiment, two successive membrane separations are carried out. More specifically: the VAP depleted gaseous stream leaving the PSA is subjected to a first membrane separation; the PSA is regenerated by means of the permeate resulting from said first membrane separation; the retentate resulting from the first separation is subjected to a second separation; Membrane separation, - the permeate from the second membrane separation is reintroduced upstream of the compression.
    Recirculation of the permeate from the second membrane separation which still contains CO2 and CH4 thus makes it possible to improve the yield of CH4. In practice, the reintroduction of the permeate is carried out between the desulfurization tank and the compressor. The next step of the process of the invention consists in carrying out an additional purification of the CO2 still present in the gas stream. Indeed, the only membrane separation is not sufficient to reach a CO2 content in the purified gas of 50 ppm before the cryogenic separation step. The value of 50 ppm is the limit value beyond which there is a risk of formation of CO2 crystals that can clog the cryogenic exchangers.
    This step is performed by a PTSA. Choosing a PTSA reduces the size of the tank and reduces cycle times. The adsorbent will in particular be selected from the group comprising zeolites.
    Advantageously, 2 PTSAs are used so as to be able to implement the process continuously. Indeed, when the first PTSA is saturated with CO2, it is substituted by the second PTSA which itself has been previously regenerated.
    The way to regenerate PTSA depends on the liquid or gaseous nature of the end product rich in methane, recovered.
    When the process aims to recover methane in liquid form, the PTSA (s) can be regenerated by means of a nitrogen flow rate resulting from the vaporization of an external source of liquid nitrogen. The steam is in this case produced by cooling the gaseous stream depleted in CO2, leaving the PTSA. This embodiment, although it can be implemented, is not optimal because it requires an additional source of liquid nitrogen.
    The process is of additional interest when it is intended to produce gaseous methane. Under these conditions: - the gas stream rich in CH4 from the cryogenic separation is vaporized; - the PTSA (s) are regenerated by means of the vaporized gas stream rich in CH4.
    Whether for the production of liquid methane or gaseous methane, another alternative is to regenerate the PTSA (s) by the N2-rich distillate resulting from the cryogenic separation, this distillate being able to be mixed with nitrogen. vaporizer for cooling the column head by spraying liquid nitrogen from an external source.
    Advantageously, the heat generated by the compression of the initial gas flow is recovered to preheat the gas flow used for the regeneration of the PTSA. Preheating thus makes it possible to raise the temperature of the gas stream from 30 to 40 ° C to a value of 80 to 90 ° C.
    The regeneration flow of the PTSA may therefore be the vaporized gas stream rich in CH4 or the N2-rich distillate from the cryogenic separation, the latter optionally being mixed in the column with the vaporized nitrogen used for cooling the column head.
    The PTSAs are designed to avoid that the biomethane produced contains more than 2.5% of CO2 in order to guarantee a quality compatible with the needs for marketing. The next step of the process of the invention consists in separating the nitrogen and ΓΟ 2 and then recovering the CH4-rich stream resulting from this separation. For this purpose, the CO2-depleted gaseous stream leaving the PTSA is subjected to cryogenic separation in a distillation column.
    In a first embodiment, the final product, that is to say the stream rich in methane, is recovered in the liquid state.
    Under these conditions: the CO2-depleted gas stream is cooled, the cooled stream is sent to the distillation column; the methane-rich liquid is withdrawn from the distillation column;
    The cooling of the flow is carried out within a heat exchanger in contact with an external source of liquid nitrogen, for example.
    In a second embodiment, the final product, that is to say the stream rich in methane, is recovered in the gaseous state.
    Under these conditions: the CO2-depleted gas stream is cooled by heat exchange with the liquid CH.sub.4 withdrawn from the distillation column; the cooled gas stream is then sent into the distillation column; the methane-rich liquid is withdrawn; of the distillation column, the methane-rich liquid is vaporized by heat exchange with the CO2-depleted gas stream from PTSA. The invention also relates to an installation for the production of bio methane by biogas purification from non-hazardous waste storage facilities (ISDND) implementing the method described above.
    In a particular embodiment, the installation comprises: a source of biogas, a compressor capable of compressing the biogas at a pressure of 8 and 24 bar, 2 PSA loaded with adsorbents capable of reversibly adsorbing the VOCs, layers of separating membranes capable of partially separating CO2 and PO2 from the gas stream, - 2 PTSA loaded with adsorbents able to reversibly adsorb most of the CO2 remaining in the gas stream, - a heat exchanger able to cool the gaseous stream depleted in CO2 a distillation column.
    The components of the installation are in fluid communication through suitable pipes. The invention and the advantages resulting therefrom will emerge from the embodiment example below, in support of the appended FIG.
    Figure 1 is a schematic representation of an installation of the invention according to a particular embodiment.
    According to this particular embodiment, the method of the invention aims to produce gaseous biomethane optimizing the energy expenditure. The plant comprises a biogas source to be treated (1), a drying unit (2), a desulfurization unit (3), a compression unit (4), a VOC purification unit (5), a first CO2 purification unit (6), a second CO2 purification unit (7), a cryodistillation unit (8), a liquid nitrogen storage unit (9), an oxidation unit (10) ) and finally a methane gas recovery unit (11). All devices are interconnected by pipes. The drying unit (2) comprises a suppressor (12) and a heat exchanger (13) and a separator pot (14). As already said, this step allows to boost from 20 to a few hundred millibars (500 mbar maximum relative) gas. Cooling the gas between 0.1 and 10 ° C allows drying. The outgoing gas stream (15) therefore has a pressure of between 20 and 500 mbar and a dew point of between 0.1 ° C. and 10 ° C. at the outlet pressure. The desulfurization unit (3) is in the form of a tank (16) loaded with activated carbons or with iron hydroxides. This unit ensures the capture of H2S and turn it into solid sulfur. The outgoing gas stream (17) in practice contains less than 5 mg / Nm3 of H2S. The compression unit (4) is in the form of a lubricated screw compressor (18). This compressor compresses the gas stream (17) at a pressure of between 8 and 24 bar. The unit further comprises a module (19) for recovering heat generated by the oil cooling circuit. The outflow is designated in Figure 1 by the reference (20). The VOC purification unit (5) comprises 2 PSAs (21, 22). They are loaded with adsorbents specifically chosen to allow the adsorption of VOCs, and their subsequent desorption during regeneration. PSAs operate alternately in production mode and regeneration mode.
    In production mode, the PSAs (21, 22) are supplied with gaseous flow at their lower part. The pipe in which the gas flow (20) flows is split into two pipes (23, 24), each equipped with a valve (25, 26) and feeding the lower part respectively of the first PSA (21) and the second PSA ( 22). The valves (25, 26) will be alternately closed depending on the saturation level of the PSAs. In practice, when the first PSA is saturated with VOC, the valve (25) is closed and the valve (26) is opened to begin charging the second PSA (22). From the upper part of each of the PSA opens a pipe respectively (27 and 28). Each of them splits into 2 pipes respectively (29, 30) and (30, 31). The purified VOC stream from the first PSA flows through the pipe (29) while the purified VOC stream from the second PSA flows through the pipe (31). The two pipes are joined to form a single pipe (51) supplying the C02 purification unit (6).
    In regeneration mode, the regenerative gas flows in the pipes (30, 32). It appears at the bottom of the PSA. Thus, a pipe (33) equipped with a valve (35) opens the first PSA (21). A pipe (34) equipped with a valve (36) opens out of the second PSA (22). The pipes (33, 34) are joined upstream of the valves (35, 36) to form a common pipe (37). This pipe is connected to the oxidation unit (10).
    The first CO2 purification unit (6) combines two membrane separation stages (38, 39). The membranes are chosen to allow the separation of about 90% of the CO2 and about 50% of ΓΟ2.
    The permeate charged with CO2, O2 and a very small proportion of CH4 from the first membrane separation is used to regenerate the PSA (21, 22). It circulates in the pipe (40) and then alternately in the pipes (30, 32) depending on the operating mode of the PSA. The retentate from the first separation is then directed to the second membrane separation (39). The permeate from the second membrane separation is recycled through a pipe connected to the main circuit upstream of the compressor (18). This step produces a gas (42) with less than 3% CO2 and a CH4 yield> 90%.
    The second CO2 purification unit (7) combines 2 PT SA (43, 44). They are loaded with adsorbents of zeolite type. They are each connected to pipes in a model identical to that of PSA previously described. They also work in a production mode or a regeneration mode. In production mode, the gas stream (42) alternately feeds the PTSAs (43, 44) through the pipes (45, 46) each equipped with a valve (47, 48). The C02 purified gas stream from the PTSA (43) then flows into the pipe (49). The CO2 purified gas stream from the PTSA (44) then flows through the pipe (50). The two pipes (49, 50) are connected in a single pipe (52) connected to the next unit.
    In regeneration mode, the regenerative gas flows in the pipes (53, 54). It appears at the bottom of the PTSA. Thus, a pipe (55) equipped with a valve (56) opens the first PTSA (43). A pipe (57) equipped with a valve (58) opens out of the second PTSA (44). The pipes (55, 57) are joined upstream of the valves (56, 58) to form a common pipe (59). This pipe is connected to the gaseous methane recovery unit (11). The cryodistillation unit (8) is fed by the pipe (52) in which circulates the gas stream to be purified. It contains 3 elements respectively a heat exchanger (60), a reboiler (61), a distillation column (62). The exchanger (60) is a brazed plate heat exchanger made of aluminum or stainless steel. It cools the gas stream (52) by heat exchange with the liquid methane stream (69) withdrawn from the distillation column (62). The gas stream (52) is partially liquefied (63). The two-phase flow (63) provides reboiling of the bottom reboiler (61) of the column (62) and the heat produced (64) is transferred to the bottom of the column (62). The stream (63) cools in the reboiler (61) and partially condenses (65). The partially condensed fluid (65) is expanded by means of a valve (66) at a pressure of between 1.1 and 5 bar absolute. The fluid then in the liquid state (67) is sent into the head of the column (62). The temperature must be higher than 90.7K to avoid solidifying the methane
    The liquid (67) then separates into the column (62) to form a gas (68) through the condenser (71). The condenser (71) is cooled by liquid nitrogen bubbling from an external source (9). The liquid nitrogen is converted into vaporized nitrogen (72). The gas (68) transfers its frigories into the exchanger (60) in contact with the gas stream (52) from PTSAs (43, 44). The gas stream obtained (70) charged with CO2 and O2 is sent to the oxidation unit (10). In the illustrated embodiment, the gas stream (70) is oxidized in a common oxidation unit (10) with the flow (37) resulting from the regeneration of PSA, charged with CO2, O2 and VOC. Alternatively, the oxidation is carried out in separate units.
    In another embodiment not shown, mixing the N2-rich distillate (68) from the cryogenic separation with the vaporized nitrogen (72) for cooling the column head (62) to regenerate the PTSA.
    The liquid (69) of the distillation column vessel (62) is fed to the reboiler (61) where it partially vaporizes. The formed gas (64) is returned to the column vessel (62). The remaining liquid (69) vaporizes in the exchanger (60) to form a pure methane gas product (73).
    In the illustrated embodiment, the gas stream (73) serves to regenerate the PTSAs (43, 44). The flow (73) is further preheated by the heat generated by the compressor oil cooling circuit (18), which passes from the module (19) through a line (74).
    According to the illustrated process, methane is recovered in the gaseous state after regeneration of PTSA. Other alternatives of the process can be envisaged, in particular that aimed at recovering liquid methane directly from the distillation column.
    权利要求:
    Claims (15)
    [1" id="c-fr-0001]
    1 / A process for producing biomethane by biogas purification from non-hazardous waste storage facilities (ISDND) according to which: - the initial gas flow is compressed, - the gas stream to be purified is introduced into at least one pressure-modulated adsorber (PSA) loaded with adsorbents capable of reversibly adsorbing VOCs, the VAP-depleted gaseous stream leaving the PSA is subjected to at least one membrane separation to partially separate the CO2 and ΓΟ 2 from the gas stream; retentate derived from the membrane separation in at least one adsorber modulated in temperature (PTSA) loaded with adsorbents able to reversibly adsorb most of the remaining CO2, the CO2-depleted gas stream leaving the PTSA is subjected to a cryogenic separation in a distillation column for separating ΓΟ2 and ΓΝ2 from the gas stream, - the CH4-rich stream resulting from the cryogenic separation is recovered.
    [0002]
    2 / A method according to claim 1, characterized in that regenerates the PSA by means of the permeate from the membrane separation.
    [0003]
    3 / A method according to one of the preceding claims, characterized in that: - the depleted VOC gas stream leaving the PSA is subjected to a first membrane separation, - regenerates the PSA by means of the permeate from said first membrane separation, - subjecting the retentate resulting from the first separation to a second membrane separation, - the permeate originating from the second membrane separation is reintroduced upstream of the compression.
    [0004]
    4 / A method according to one of the preceding claims, characterized in that: - the gas stream rich in CH4 from the cryogenic separation is vaporized; - the PTSA (s) is regenerated by means of the vaporized gas stream rich in CH4.
    [0005]
    5 / A method according to one of claims 1 to 3, characterized in that regenerates the PTSA with N2-rich distillate from the cryogenic separation.
    [0006]
    6 / A method according to one of the preceding claims, characterized in that maintains the distillation column head by vaporization of liquid nitrogen from an external source.
    [0007]
    7 / A method according to claims 5 and 6, characterized in that in the column mixed the N2-rich distillate from the cryogenic separation with vaporized nitrogen for cooling the column head and then regenerates the PTSA with said mixed.
    [0008]
    8 / A method according to one of claims 2 to 7, characterized in that the oxide gas stream from the regeneration of the PSA is oxidized.
    [0009]
    9 / A method according to one of claims 1 to 7, characterized in that oxide distillate N2 rich from the cryogenic separation.
    [0010]
    10 / A method according to claims 8 and 9, characterized in that the two gas flows before the oxidation.
    [0011]
    11 / A method according to one of claims 2 to 10, characterized in that recovering the heat generated by the compression of the initial gas flow to preheat the gas stream for the regeneration of PTSA.
    [0012]
    12 / A method according to one of the preceding claims, characterized in that the compression step is preceded by a desulfurization step.
    [0013]
    13 / A method according to claim 12, characterized in that prior to the desulfurization step, the gas stream is dried.
    [0014]
    14 / Plant for the production of bio methane by purification of biogas from non-hazardous waste storage facilities (ISDND) implementing the method according to one of the preceding claims.
    [0015]
    15 / Plant for the production of bio methane by purification of biogas from non-hazardous waste storage facilities (ISDND) successively comprising: - a source of biogas (1) - a compressor (18) capable of compressing the biogas to a pressure of 8 and 24 bars, - 2 PSA (21, 22) charged with adsorbents capable of reversibly adsorbing VOCs, - 2 stages of separating membranes (38, 39) capable of partially separating the CO2 and ΙΌ 2 from the gas stream, - 2 PTS A (43, 44) charged with adsorbents capable of reversibly adsorbing most of the CO2 remaining in the gas stream, - a heat exchanger (60) capable of cooling the gas stream depleted in CO2, - a distillation column (62). ).
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    同族专利:
    公开号 | 公开日
    BR112018012788A2|2018-12-04|
    PT3393621T|2022-01-12|
    EP3393621A1|2018-10-31|
    RU2721698C2|2020-05-21|
    RU2018122940A|2020-01-24|
    HK1256981A1|2019-10-11|
    MX2018007771A|2019-01-10|
    FR3046086B1|2018-01-05|
    WO2017109305A1|2017-06-29|
    RU2018122940A3|2020-01-24|
    AU2016378831A1|2018-07-12|
    DK3393621T3|2022-01-17|
    US20190001263A1|2019-01-03|
    AU2016378831B2|2021-12-09|
    CA3009566A1|2017-06-29|
    US10905995B2|2021-02-02|
    CN108602007A|2018-09-28|
    EP3393621B1|2022-01-05|
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    法律状态:
    2016-12-23| PLFP| Fee payment|Year of fee payment: 2 |
    2017-06-30| PLSC| Publication of the preliminary search report|Effective date: 20170630 |
    2017-12-23| PLFP| Fee payment|Year of fee payment: 3 |
    2019-12-27| PLFP| Fee payment|Year of fee payment: 5 |
    2020-12-29| PLFP| Fee payment|Year of fee payment: 6 |
    2021-12-28| PLFP| Fee payment|Year of fee payment: 7 |
    优先权:
    申请号 | 申请日 | 专利标题
    FR1563357A|FR3046086B1|2015-12-24|2015-12-24|PROCESS FOR PRODUCING BIOMETHANE BY PURIFYING BIOGAS FROM NON-HAZARDOUS WASTE STORAGE FACILITIESAND INSTALLATION FOR IMPLEMENTING THE METHOD|
    FR1563357|2015-12-24|FR1563357A| FR3046086B1|2015-12-24|2015-12-24|PROCESS FOR PRODUCING BIOMETHANE BY PURIFYING BIOGAS FROM NON-HAZARDOUS WASTE STORAGE FACILITIESAND INSTALLATION FOR IMPLEMENTING THE METHOD|
    PCT/FR2016/052937| WO2017109305A1|2015-12-24|2016-11-10|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method|
    EP16809983.6A| EP3393621B1|2015-12-24|2016-11-10|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method|
    MX2018007771A| MX2018007771A|2015-12-24|2016-11-10|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method.|
    CN201680079846.6A| CN108602007A|2015-12-24|2016-11-10|By purifying the method for the biogas production biological methane from unhazardous waste storage facility and implementing the facility of this method|
    RU2018122940A| RU2721698C2|2015-12-24|2016-11-10|Method of producing biomethane by cleaning biogas from non-hazardous wastes and apparatus for realizing the method|
    PT168099836T| PT3393621T|2015-12-24|2016-11-10|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method|
    US16/065,644| US10905995B2|2015-12-24|2016-11-10|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method|
    DK16809983.6T| DK3393621T3|2015-12-24|2016-11-10|Process for the production of biomethane by purification of biogas from plants for storage of non-hazardous waste and plants for carrying out the process|
    BR112018012788-4A| BR112018012788A2|2015-12-24|2016-11-10|Method and installation for producing biogas purification biomethane from non-hazardous waste storage facilities|
    CA3009566A| CA3009566A1|2015-12-24|2016-11-10|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method|
    AU2016378831A| AU2016378831B2|2015-12-24|2016-11-10|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method|
    HK18115950.6A| HK1256981A1|2015-12-24|2018-12-12|Method for producing biomethane by purifying biogas from non-hazardous waste storage facilities and facility for implementing the method|
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